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KRIS E. Marin Sonoma: Chart Source Table Page
Area | Novato and Miller Creeks |
Topic | Habitat: Physical Habitat Quality Scores in Miller Creek 2000 |
Caption: The Source Table inverthab_all_mcdpw_1999_2002.xls.db shows the results of benthic macroinvertebrate sampling and habitat assessments conducted during September 1999, April 2000, and Spring 2002 at several sites in east Marin County watersheds. The metrics included in the table are the mean values for Taxonomic Richness (TAXARICH), Percent Dominant Taxon (PCTDOM), EPT Taxa (EPTTAXA), Modified EPT (MODEPT), Shannon Diversity (SHANNON), and Tolerance Value (TOLVALUE), along with the associated Index of Biological Integrity (IBI) score for each metric as well as the total IBI (IBI_TOTSCORE) and rank (IBIRANK). In addition, EPT Index (EPTINDEX) is also included. The habitat parameters include instream cover (INSTCOV), embeddedness (EMBEDD), velocity/depth (VELDEPTH), sediment deposition (SEDDEP), channel flow (CHANFLOW), channel alteration (CHANALT), riffle frequency (RIFFREQ), bank stability (BANKSTAB), vegetative protection (VEGPROT), riparian vegetative zone width (RIPVEG), total reach score (REACHTOT), condition (CONDITION), percent vegetative canopy cover estimate (VEGCANOP), water temperature in C (WATTEMP), specific conductance in uS/cm at 25 C (SPECCOND), and comments pertinent to the habitat assessment (HABCOMMENTS). Click on Map to view the sampling locations. Data were collected and analyzed by the Sustainable Land Stewardship Institute and provided by the Marin County Department of Public Works.
50 rows of a possible 660 have been displayed.
WATERSHED | LOCATION | SITE | TAXARICH_99 | IBI_TAXARICH_99 | PCTDOM_99 | IBI_PCTDOM_99 | EPTTAXA_99 | IBI_EPTTAXA_99 | MODEPT_99 | IBI_MODEPT_99 | SHANNON_99 | IBI_SHANNON_99 | TOLVALUE_99 | IBI_TOLVALUE_99 | IBI_TOTSCORE_99 | IBIRANK_99 | TAXARICH_00 | IBI_TAXARICH_00 | PCTDOM_00 | IBI_PCTDOM_00 | EPTTAXA_00 | IBI_EPTTAXA_00 | MODEPT_00 | IBIMODEPT_00 | SHANNON_00 | IBI_SHANNON_00 | TOLVALUE_00 | IBI_TOLVALUE_00 | IBI_TOTSCORE_00 | IBIRANK_00 | EPTINDEX_99 | EPTINDEX_00 | COMMENTS | TAXARICH_02 | PCTDOM_02 | EPTTAXA_02 | EPTINDEX_02 | SHANNON_02 | TOLVALUE_02 | INSTRCOV_99 | INSTRCOV_00 | EMBEDD_99 | EMBEDD_00 | VELDEPTH_99 | VELDEPTH_00 | SEDDEP_99 | SEDDEP_00 | CHANFLOW_99 | CHANFLOW_00 | CHANALT_99 | CHANALT_00 | RIFFREQ_99 | RIFFREQ_00 | BANKSTAB_99 | BANKSTAB_00 | VEGPROT_99 | VEGPROT_00 | RIPVEG_99 | RIPVEG_00 | REACHTOT_99 | REACHTOT_00 | CONDITION_99 | CONDITION_00 | VEGCANOP_99 | VEGCANOP_00 | WATTEMP_99 | WATTEMP_00 | SPECCOND_99 | SPECCOND_00 | HABCOMMENTS_99 | HABCOMMENTS_00 |
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Arroyo Corte Madera del Presidio | Arroyo Corte Madera del Presidio | ACM1 | 16 | 1 | 42 | 1 | 2 | - | 5 | 1 | 1.7 | 1 | 5.8 | 1 | 6 | poor | 9 | 1 | 65 | 1 | 2 | 1 | 0 | 1 | 1 | 1 | 6.1 | 1 | 6 | poor | 32 | 6 | - | 10 | 64 | 2 | 65 | 1.1 | 5.6 | 8 | 12 | 12 | 15 | 12 | 14 | 10 | 15 | 5 | 13 | 8 | 9 | 16 | 14 | 12 | 13 | 10 | 8 | 4 | 5 | 97 | 118 | marginal | suboptimal | 26 | 15 | 15 | 12 | 280 | 161 | stormdrain @ riffle 2 | water turbid |
Arroyo Corte Madera del Presidio | Arroyo Corte Madera del Presidio | ACM2 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 24 | 1 | 26 | 3 | 10 | 1 | 29 | 3 | 2.2 | 1 | 4.3 | 3 | 12 | fair | - | 36 | - | - | - | - | - | - | - | - | 10 | - | 17 | - | 12 | - | 17 | - | 10 | - | 5 | - | 16 | - | 18 | - | 5 | - | 4 | - | 114 | - | suboptimal | - | 73 | - | 12 | - | 165 | - | water turbid, some foam, stormdrain between r-2 & 3 |
Arroyo Corte Madera del Presidio | Arroyo Corte Madera del Presidio | ACM3 | 31 | 3 | 25 | 3 | 17 | 3 | 48 | 3 | 2.7 | 3 | 3.5 | 3 | 18 | good | 29 | 3 | 19 | 3 | 13 | 3 | 22 | 3 | 2.8 | 3 | 4.5 | 3 | 18 | good | 34 | 60 | - | - | - | - | - | - | - | 16 | 18 | 17 | 17 | 16 | 15 | 17 | 17 | 6 | 11 | 16 | 16 | 18 | 18 | 19 | 17 | 17 | 13 | 16 | 14 | 158 | 156 | optimal | optimal | 80 | 68 | 16 | 12 | 200 | 153 | Pacific giant salamander larvae | Pacific giant salamander larvae, stormdrain between r-2 & 3 |
Arroyo Corte Madera del Presidio | Old Mill Creek | ACM4 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 19 | 1 | 30 | 3 | 9 | 1 | 18 | 3 | 2.1 | 1 | 5.1 | 1 | 7 | poor | - | 26 | - | 20 | 40 | 5 | 40 | 1.8 | 4.9 | - | 15 | - | 17 | - | 15 | - | 15 | - | 8 | - | 15 | - | 18 | - | 10 | - | 11 | - | 12 | - | 136 | - | suboptimal | - | 58 | - | 12 | - | 173 | - | stormdrain below r-1, bareground in park source of sediment |
Arroyo Corte Madera del Presidio | Old Mill Creek | ACM5 | 25 | 1 | 21 | 3 | 11 | 1 | 25 | 3 | 2.7 | 3 | 4.2 | 3 | 14 | fair | 26 | 3 | 31 | 3 | 12 | 3 | 14 | 1 | 2.4 | 3 | 4.9 | 1 | 14 | fair | 39 | 18 | - | 25 | 34 | 10 | 56 | 2.2 | 4.2 | 15 | 16 | 17 | 17 | 15 | 15 | 17 | 17 | 7 | 9 | 18 | 15 | 18 | 18 | 16 | 15 | 15 | 15 | 18 | 16 | 156 | 153 | optimal | optimal | 86 | 77 | 13 | 13 | 560 | 150 | 10cm crayfish released, Pacific giant salamander larvae | - |
Corte Madera Creek | Corte Madera Creek | CM1 | 17 | 1 | 36 | 3 | 3 | 1 | 1 | 1 | 2 | 1 | 5.5 | 1 | 8 | poor | 12 | 1 | 74 | 1 | 2 | 1 | 0 | 1 | 1 | 1 | 5.4 | 1 | 6 | poor | 13 | 2 | - | 16 | 51 | 3 | 8 | 1.4 | 6.7 | 8 | 8 | 12 | 11 | 9 | 9 | 5 | 8 | 5 | 8 | 11 | 14 | 8 | 14 | 16 | 17 | 17 | 16 | 13 | 13 | 104 | 116 | suboptimal | suboptimal | 32 | 43 | 16 | 15 | - | 330 | - | - |
Corte Madera Creek | Corte Madera Creek | CM2 | 17 | 1 | 34 | 3 | 4 | 1 | 7 | 1 | 2 | 1 | 5.6 | 1 | 8 | poor | 15 | 1 | 48 | 1 | 7 | 1 | 5 | 1 | 1.6 | 1 | 5.2 | 1 | 6 | poor | 10 | 18 | - | 12 | 43 | 1 | 43 | 1.5 | 5.8 | 7 | 10 | 12 | 12 | 7 | 14 | 9 | 9 | 7 | 10 | 6 | 6 | 3 | 5 | 16 | 18 | 9 | 10 | 6 | 6 | 82 | 100 | marginal | marginal | 78 | 63 | 15 | 15 | - | 370 | - | r-2 under bridge abutment |
Corte Madera Creek | Ross Creek | CM3 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 21 | 1 | 37 | 3 | 7 | 1 | 11 | 1 | 2.1 | 1 | 5.3 | 1 | 8 | poor | - | 23 | - | - | - | - | - | - | - | - | 17 | - | 12 | - | 15 | - | 18 | - | 9 | - | 20 | - | 17 | - | 18 | - | 16 | - | 19 | - | 161 | - | optimal | - | 72 | - | 16 | - | 162 | - | reach may be missing sand substrate |
Corte Madera Creek | Billy Williams Creek | CM3b | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 30 | 3 | 23 | 3 | 18 | 3 | 44 | 3 | 2.6 | 3 | 3.7 | 3 | 18 | good | - | 64 | - | - | - | - | - | - | - | - | 14 | - | 18 | - | 15 | - | 17 | - | 6 | - | 20 | - | 17 | - | 18 | - | 18 | - | 20 | - | 163 | - | optimal | - | 77 | - | 11 | - | 155 | - | Pacific giant salamander |
Corte Madera Creek | San Anselmo Creek | CM4 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 20 | 1 | 53 | 1 | 9 | 1 | 4 | 1 | 1.7 | 1 | 5.3 | 1 | 6 | poor | - | 12 | - | 9 | 49 | 1 | 4 | 1.3 | 5.8 | - | 15 | - | 14 | - | 15 | - | 14 | - | 14 | - | 15 | - | 6 | - | 11 | - | 13 | - | 7 | - | 124 | - | suboptimal | - | 42 | - | 13 | - | 188 | - | sculpin. stormdrain under u/s r-3 |
Corte Madera Creek | Sleepy Hollow Creek | CM5 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 11 | 1 | 43 | 1 | 2 | 1 | 1 | 1 | 1.5 | 1 | 5.3 | 1 | 6 | poor | - | 7 | - | - | - | - | - | - | - | - | 15 | - | 13 | - | 15 | - | 15 | - | 11 | - | 15 | - | 14 | - | 14 | - | 16 | - | 10 | - | 138 | - | suboptimal | - | 48 | - | 13 | - | 358 | - | - |
Corte Madera Creek | Sleepy Hollow Creek | CM6 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 9 | 1 | 61 | 1 | 2 | 1 | 1 | 1 | 1.2 | 1 | 5.4 | 1 | 6 | poor | - | 8 | - | - | - | - | - | - | - | - | 13 | - | 12 | - | 13 | - | 12 | - | 7 | - | 9 | - | 11 | - | 15 | - | 13 | - | 6 | - | 111 | - | suboptimal | - | 60 | - | 14 | - | 520 | - | low water. filamentous algae. 4 stormdrains in reach. R-3 under house |
Corte Madera Creek | Sleepy Hollow Creek | CM7 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 17 | 1 | 64 | 1 | 9 | 1 | 11 | 1 | 1.5 | 1 | 4.8 | 1 | 6 | poor | - | 18 | - | 17 | 51 | 5 | 34 | 1.5 | 4.9 | - | 15 | - | 12 | - | 14 | - | 14 | - | 7 | - | 10 | - | 11 | - | 14 | - | 15 | - | 9 | - | 121 | - | suboptimal | - | 47 | - | 12 | - | 347 | - | - |
Corte Madera Creek | Sleepy Hollow Creek | CM7b | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 18 | 1 | 40 | 1 | 10 | 1 | 50 | 5 | 1.9 | 1 | 3.6 | 3 | 12 | fair | - | 86 | - | 18 | 52 | 3 | 26 | 1.6 | 5.1 | - | 8 | - | 12 | - | 11 | - | 17 | - | 12 | - | 19 | - | 17 | - | 16 | - | 19 | - | 14 | - | 145 | - | suboptimal | - | 37 | - | 13 | - | 307 | - | algae. minimal flow. wild bamboo. scotch/franch broom. |
Corte Madera Creek | San Anselmo Creek | CM8 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 24 | 1 | 27 | 3 | 12 | 3 | 34 | 3 | 2.4 | 3 | 4.2 | 1 | 14 | fair | - | 42 | - | 14 | 44 | 5 | 39 | 1.4 | 5.2 | 12 | 9 | 14 | 17 | 12 | 13 | 7 | 5 | 7 | 8 | 14 | 12 | 14 | 15 | 16 | 16 | 14 | 16 | 14 | 10 | 124 | 121 | suboptimal | suboptimal | 53 | 47 | 15 | 13 | - | 276 | sculpin in r-4, many yoy fingerling | heavy sediment behind dam. yoy trout. sculpin. riffle sculpin. |
Corte Madera Creek | San Anselmo Creek | CM8b | 18 | 1 | 42 | 1 | 4 | 1 | 12 | 1 | 1.9 | 1 | 4.9 | 1 | 6 | poor | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 15 | - | CM-8 excluded transects 4 and 5 from CRT, mean, and CV calculations. | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - |
Corte Madera Creek | Cascade Creek | CM9 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 13 | 1 | 40 | 1 | 12 | 3 | 77 | 5 | 2 | 1 | 2.1 | 5 | 16 | fair | - | 80 | - | - | - | - | - | - | - | - | 16 | - | 16 | - | 16 | - | 14 | - | 11 | - | 17 | - | 14 | - | 13 | - | 16 | - | 11 | - | 144 | - | suboptimal | - | 63 | - | 15 | - | 265 | - | - |
Corte Madera Creek | Cascade Creek | CM10 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 27 | 3 | 18 | 3 | 17 | 3 | 44 | 3 | 2.7 | 3 | 3 | 5 | 20 | good | - | 64 | - | - | - | - | - | - | - | 12 | 17 | 18 | 17 | 11 | 15 | 17 | 18 | 4 | 8 | 20 | 19 | 18 | 16 | 15 | 17 | 15 | 18 | 18 | 19 | 148 | 164 | suboptimal | optimal | 90 | 77 | 14 | 12.5 | - | 305 | spotsampled due to possible steelhead habitat | - |
Miller Creek | Miller Creek | MC1 | 19 | 1 | 28 | 3 | 5 | 1 | 15 | 1 | 2.2 | 1 | 5.2 | 1 | 8 | poor | 9 | 1 | 42 | 1 | 2 | 1 | 1 | 1 | 1.5 | 1 | 5.6 | 1 | 6 | poor | - | - | - | - | - | - | - | - | - | 12 | 13 | 14 | 14 | 14 | 11 | 12 | 16 | 5 | 9 | 19 | 17 | 15 | 16 | 18 | 15 | 16 | 13 | 14 | 15 | 139 | 139 | suboptimal | suboptimal | 70 | 65 | 62 | - | 354 | 360 | Stormdrain between riffle 1 and 2; residence on left bank; minimal flow for sampling | stormdrain r-2 |
Miller Creek | Miller Creek | MC2 | 19 | 1 | 29 | 3 | 4 | 1 | 19 | 3 | 2.1 | 1 | 5 | 1 | 10 | poor | 9 | 1 | 53 | 1 | 2 | 1 | 0 | 1 | 1.3 | 1 | 5 | 1 | 6 | poor | - | - | - | - | - | - | - | - | - | 14 | 18 | 13 | 15 | 15 | 16 | 11 | 10 | 7 | 9 | 18 | 18 | 15 | 17 | 15 | 14 | 16 | 14 | 14 | 14 | 138 | 145 | suboptimal | suboptimal | 70 | 80 | 62 | - | 332 | 340 | Bridge abutments, residences and school within or near riparian zone; minimal flow for sampling | school nearby. stormdrain d/s r-1 |
Miller Creek | Miller Creek | MC3 | 19 | 1 | 30 | 3 | 5 | 1 | 16 | 1 | 2.3 | 3 | 5 | 1 | 10 | poor | 15 | 1 | 53 | 1 | 5 | 1 | 3 | 1 | 1.5 | 1 | 5.1 | 1 | 6 | poor | - | - | - | - | - | - | - | - | - | 13 | 15 | 14 | 11 | 14 | 15 | 14 | 13 | 8 | 11 | 18 | 18 | 15 | 12 | 14 | 14 | 14 | 14 | 15 | 16 | 139 | 139 | suboptimal | suboptimal | 85 | 70 | 61 | - | 294 | 310 | Stormdrain on right bank upstream of riffle 1; trails within riparian zone | stormdrain u/s r-5 |
Miller Creek | Miller Creek | MC4 | 23 | 1 | 27 | 3 | 8 | 1 | 11 | 1 | 2.5 | 3 | 5.4 | 1 | 10 | poor | 20 | 1 | 36 | 3 | 12 | 3 | 19 | 3 | 2 | 1 | 4.7 | 1 | 12 | fair | - | - | - | 15 | 37 | 4 | 16 | 1.7 | 5.9 | 17 | 19 | 16 | 14 | 16 | 17 | 13 | 13 | 7 | 10 | 20 | 19 | 17 | 18 | 18 | 18 | 19 | 20 | 18 | 18 | 161 | 166 | optimal | optimal | 50 | 47 | 60 | - | 273 | 280 | Overall good quality site but minimal flow for sampling; samples collected under blackberry vines; recommend frog surveys for this site | - |
Miller Creek | Miller Creek | MC5 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 19 | 1 | 56 | 1 | 10 | 1 | 25 | 3 | 1.6 | 1 | 4.4 | 3 | 10 | poor | - | - | - | 14 | 48 | 2 | 25 | 1.5 | 5.3 | - | 13 | - | 12 | - | 14 | - | 12 | - | 7 | - | 19 | - | 16 | - | 18 | - | 14 | - | 16 | - | 141 | - | suboptimal | - | 17 | - | - | - | 220 | - | stormdrain @ upper end reach |
Miller Creek | Miller Creek | MC6 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 23 | 1 | 37 | 3 | 15 | 3 | 44 | 3 | 2.1 | 1 | 3.6 | 3 | 14 | fair | - | - | - | - | - | - | - | - | - | - | 13 | - | 17 | - | 14 | - | 12 | - | 7 | - | 18 | - | 18 | - | 5 | - | 8 | - | 14 | - | 126 | - | suboptimal | - | 20 | - | - | - | 210 | - | yoy trout. stream dry u/s of bridge @ top of riffle |
Miller Creek | Miller Creek | MC9 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 17 | 52 | 7 | 43 | 1.3 | 4.9 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - |
Novato Creek | Novato Creek | NC1 | 22 | 1 | 31 | 3 | 67 | 1 | 25 | 3 | 2.3 | 3 | 4.9 | 1 | 12 | poor | 10 | 1 | 67 | 1 | 4 | 1 | 2 | 1 | 1.1 | 1 | 5.4 | 1 | 6 | poor | 67 | 9 | - | - | - | - | - | - | - | 12 | 12 | 12 | 15 | 15 | 15 | 16 | 12 | 7 | 10 | 20 | 16 | 15 | 14 | 18 | 14 | 16 | 17 | 14 | 14 | 145 | 139 | suboptimal | suboptimal | 50 | 64 | 57 | 12 | 440 | 440 | Stormdrain upstream of riffle 6. Low flow in reach | sheen on water surface. petroleum smell. stormdrain u/s r-2 |
Novato Creek | Novato Creek | NC2 | 23 | 1 | 33 | 3 | 6 | 1 | 20 | 3 | 2.4 | 3 | 4.9 | 1 | 12 | fair | 16 | 1 | 38 | 3 | 6 | 1 | 9 | 1 | 1.8 | 1 | 5.4 | 1 | 8 | poor | 57 | 22 | - | - | - | - | - | - | - | 8 | 12 | 12 | 12 | 9 | 12 | 11 | 12 | 7 | 10 | 20 | 16 | 12 | 16 | 16 | 15 | 15 | 16 | 15 | 14 | 125 | 135 | suboptimal | suboptimal | 70 | 77 | 57 | 13 | 420 | 460 | Sinola Environmental Club was doing a stream clean-up during our sampling. Low flow in reach | outfall between r-1 & 2 |
Novato Creek | Novato Creek | NC3 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 20 | 1 | 30 | 3 | 9 | 1 | 17 | 3 | 2.2 | 1 | 5.1 | 1 | 10 | poor | - | 45 | - | 13 | 50 | 2 | 4 | 1.4 | 7.7 | - | 16 | - | 12 | - | 16 | - | 10 | - | 9 | - | 18 | - | 12 | - | 12 | - | 14 | - | 14 | - | 133 | - | suboptimal | - | 62 | - | 14 | - | 420 | - | stormdrain u/s of t-3 & d/s t-2. fish in pool. |
Novato Creek | Novato Creek | NC4 | 21 | 1 | 24 | 3 | 8 | 1 | 21 | 3 | 2.4 | 3 | 4.5 | 3 | 14 | fair | 23 | 1 | 41 | 1 | 10 | 1 | 14 | 1 | 2.1 | 1 | 4.9 | 1 | 6 | poor | 61 | 60 | - | 17 | 41 | 3 | 2 | 1.6 | 7.3 | 15 | 13 | 14 | 14 | 17 | 15 | 13 | 13 | 7 | 8 | 20 | 20 | 18 | 18 | 17 | 12 | 16 | 16 | 20 | 18 | 157 | 147 | optimal | suboptimal | 60 | 75 | 59 | 14 | 330 | 410 | Mitten crab found in reach; overall good quality reach except for low flow conditions | - |
Novato Creek | Novato Creek | NC5 | 24 | 1 | 22 | 3 | 10 | 1 | 20 | 3 | 2.5 | 3 | 4.6 | 3 | 14 | fair | 22 | 1 | 24 | 3 | 9 | 1 | 7 | 1 | 2.2 | 1 | 5.5 | 1 | 8 | poor | 58 | 27 | - | - | - | - | - | - | - | 13 | 11 | 12 | 11 | 15 | 13 | 12 | 9 | 5 | 6 | 20 | 20 | 16 | 16 | 11 | 10 | 12 | 12 | 19 | 18 | 135 | 126 | suboptimal | suboptimal | 70 | 72 | 64 | 15 | 290 | 520 | Low flow in reach | overall poor riffle habitat |
Novato Creek | Novato Creek | NC6 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 17 | 1 | 29 | 3 | 9 | 1 | 39 | 3 | 2 | 1 | 3.6 | 3 | 12 | fair | - | 63 | - | - | - | - | - | - | - | - | 14 | - | 14 | - | 15 | - | 14 | - | 6 | - | 20 | - | 16 | - | 18 | - | 18 | - | 20 | - | 155 | - | optimal | - | 33 | - | 16 | - | 350 | - | SF garter snake on path |
Novato Creek | Warner Creek | NC7 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 13 | 1 | 39 | 3 | 4 | 1 | 6 | 1 | 1.7 | 1 | 5.7 | 1 | 8 | poor | - | 8 | - | 13 | 56 | 1 | 1 | 1.3 | 6.3 | - | 11 | - | 12 | - | 14 | - | 15 | - | 6 | - | 17 | - | 17 | - | 14 | - | 14 | - | 9 | - | 129 | - | suboptimal | - | 57 | - | 15 | - | 490 | - | stormdrain u/s r-8 |
Novato Creek | Warner Creek | NC8 | 19 | 1 | 28 | 3 | 4 | 1 | 6 | 1 | 2.1 | 1 | 5.8 | 1 | 8 | poor | 10 | 1 | 39 | 3 | 2 | 1 | 0 | 1 | 1.4 | 1 | 6.3 | 1 | 8 | poor | 26 | 2 | - | - | - | - | - | - | - | 10 | - | 6 | - | 8 | - | 12 | - | 6 | - | 7 | - | 10 | - | 16 | - | 12 | - | 6 | - | 93 | - | maginal | - | 30 | - | 63 | - | 580 | - | Substrate mostly hardpan clay; banks stabilized w/ concrete bags | - |
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